San Antonio River Authority Westside Creeks/Elmendorf Lake Final Report June 2012 ACKNOWLEDGEMENTS Acknowledgements Malcolm Pirnie/ARCADIS, Terra Design Group and RTKL wish to thank the San Antonio River Authority for the opportunity to work on this extremely important project. We also thank SARA and its partners, Bexar County, the City of San Antonio and Our Lady of the Lake University, for the tremendous amount of assis- tance and support during the evaluation and planning processes. We greatly appreciate the thorough and timely input provided by each of the organizations during the development of the alternatives, conceptual plans and the final report. At the risk of overlooking someone, we express our appreciation to Project Manager Rudy Farias and the other professional staff members who greatly assisted the study team by attending the initial visioning workshop and assisting in the development of a Vision for a Great People Place in the Westside. San Antonio River Authority Suzanne Scott Rudy Farias Gloria Rodriquez Brian Mast Russell Persyn Bob Perez Bexar County Renee Green Kerim Jacaman City of San Antonio Xavier Urrutia Natalie Balderrama Nefi Garza Brandon Ross Homer Garcia Bill Pannell Rodney Dziuk Our Lady of the Lake University David Estes Darrell Glasscock 2 San Antonio River Authority Westside Creeks/Elmendorf Lake Final Report July 2012 TABLE OF CONTENTS Table of Contents Section 1. Executive Summary 6 1.1 Introduction 6 1.2 Existing Conditions 6 1.3 H&H Analysis and Flood Mitigation Recommendations 6 1.4 Water Quality Analysis 7 1.5 Stormwater Best Management Practices 9 1.6 Vision Plan 10 1.7 Cost Estimate and Allocation of Cost 12 1.8 Conclusions and Recommendations 12 Section 2. Introduction 15 Section 3. Existing Conditions 19 3.1 History of Elmendorf Dam and Lake 19 3.2 Description of Apache Creek and Elmendorf Lake 22 3.3 Description of Study Area 22 Section 4. Hydrologic and Hydraulics Analysis and Flood Mitigation Recommendations 25 4.1 Introduction and Background 25 4.2 Existing Conditions Hydrology 25 4.3 Existing Condition Hydraulics 26 4.4 Proposed Alternatives for Flood Mitigation 29 4.5 Conclusions 34 Section 5. Water Quality Analysis and Recommendations 36 5.1 Introduction 36 5.2 Background and Approach 36 5.3 Summary of Water Quality Data 38 5.4 Options to Improve Water Quality 45 5.5 Recommendations 54 5.6 References 55 Section 6. Stormwater Best Management Practices 57 6.1 Source Controls 57 6.2 Structural Controls 60 6.3 Other Municipal Operations 62 6.4 In-reservoir Debris Removal Systems 66 6.5 Effectiveness 69 6.6 Low Impact Development Practices 70 6.7 References 71 3 San Antonio River Authority Westside Creeks/Elmendorf Lake Final Report July 2012 TABLE OF CONTENTS Table of Contents Section 7. Vision Plan 73 7.1. Introduction and Existing Conditions 73 7.2 Connectivity 79 7.3 Elmendorf Lake Park Plan 83 7.4 Bexar County Participation 95 7.5 Private Participation 96 Section 8. Cost Estimates and Allocation of Cost 102 Section 9. Conclusions and Recommendations 109 9.1. Introduction 109 9.2 Flood Mitigation 109 9.3 Water Quality 110 9.4 Sustainable Best Management Practices (BMPs) 111 9.5 Vision Plan 112 Attachment 1. Elmendorf Lake Profile Comparison 115 Attachment 2. SolarBee Quote 118 Appendix A. Public Meeting - June 19, 2012 Memorandum 126 4 San Antonio River Authority Westside Creeks/Elmendorf Lake Final Report July 2012 Section 1: Executive Summary SECTION 1 Executive Summary 1. Executive Summary 1.1 Introduction The San Antonio River Authority (SARA) has recently completed the Westside Creeks Restoration Project Conceptual Plan (the “Conceptual Plan”) and in June 2011 the Conceptual Plan was adopted by the SARA Board of Directors. One of the first creek segments planned for implementation is Apache Creek Reach No. 1 which lies between North General McMullen Drive and Southwest 19th Street). This reach is essen- tially the entirety of Elmendorf Lake, including the dam. See Figure 2.1 in the final report. As SARA and its partners (including Bexar County, the City of San Antonio, and Our Lady of the Lake University) move forward with implementation of the Conceptual Plan, there are a number of additional activities, studies and plans that must be considered. SARA and its partners wish to create a vision within the Elmendorf Lake area that produces a “Great People Place in the Westside” based upon these various studies, as well as additional community input. Therefore, on August 30, 2011 SARA engaged Malcolm Pirnie, the Water Division of ARCADIS-US, to use existing hydrologic and hydraulic (H&H) models, and other tools to review the existing studies, plans and projects in order to: • Evaluate the flood mitigation benefits of the Dredging Project and channel modification projects pro- posed in the Conceptual Plan, and determine the potential benefits of projects proposed in the Upper San Antonio River Master Plan; • Determine opportunities to refine the existing plans to make them more cohesive and integrated; • Determine opportunities to link the current plans with other facilities and features in the area; • Verify and validate cost estimates and look for potential savings; • Perform an cursory evaluation of the Dredging Project to see if there are ways to achieve the same results without dredging portions of Elmendorf Lake or in the alternative, to reduce the costs of the Dredging Project; • Develop a preliminary conceptual plan for improvements to Elmendorf Lake Park; and • Produce a set of graphics that accurately and clearly describe the vision for the Elmendorf Lake area. 1.2 Existing Conditions The history of Elmendorf Lake is linked directly to the history of Our Lady of the Lake University (OLLU) and the local Westside Community. OLLU, a private Catholic university, was founded in 1895. The stu- dents and faculty have been using Apache Creek and the lake since that time. Elmendorf Lake Dam is a labyrinth weir structure constructed in 1974. The total effective length of the weir is 1,700 feet, and the height is approximately 12 feet. The dam does not have a service or emergen- cy spillway. There are a series of outlet pipes through the weir that are controlled by individual manually- operated gate valves. Although the Conceptual Plan refers primarily to Apache Creek, the upstream end of the lake is actually on Zarzamora Creek. Zarzamora Creek provides most of the drainage area for the lake. Another major tribu- tary to the lake is Bandera Branch. Within the main body of Elmendorf Lake an island runs with the length of the lake generally between 24th Street and the dam. 1.3 H&H Analysis and Flood Mitigation The most recent comprehensive hydrology study of Apache Creek and its tributaries was completed in 2006 as part of the Upper San Antonio River Flood Insurance Rate Map (FIRM) updates, published by 6 San Antonio River Authority Westside Creeks/Elmendorf Lake Final Report July 2012 SECTION 1 Executive Summary FEMA. This effective hydrology model was also the basis for the Conceptual Plan and the Upper San Antonio River Watershed Masterplan both published in June 2011. The study teams analysis of the effective hydrology model consisted of a review of the methodology, du- plication of the effective model results, and verification of the effective flows calculated in HEC-HMS using regression equations. The extent of this review was limited to the drainage area from Elmendorf Lake Dam to General McMullen Drive. HEC-HMS model results show the effective peak 100-year (1%) discharge at the confluence of Apache Creek and Zarzamora Creek is 24,724 cubic feet per second (cfs). The effective peak 100-year discharge immediately downstream of the 24th Street bridge is 25,307 cfs. During the workshop held on August 31, 2011 with SARA and its partners, the goal with regard to flood mitigation was identified as “100-year flood protection for structures around the lake.” This goal was used to guide the identification and evaluation of alternatives to lower the peak water elevation during major flood events. The following three alternatives were identified and evaluated in some detail during the de- velopment of the plan for Elmendorf Lake Park: • Alternative 1 – Re-grading portions of Rosedale Park and across Zarzamora Creek south to Faust Street for flood storage • Alternative 2 – Re-grading portions of Rosedale Park along Apache Creek for flood storage • Alternative 3 – Constructing for flood storage a diversion channel through the existing levee on the north side of Zarzamora Creek Several other alternatives were considered but not studied in as much detail. These included additional storage upstream of General McMullen Drive and adding additional discharge capacity at Elmendorf Lake Dam. This might be achieved through construction of a side channel spillgate. At SARA’s request, the proposed condition with dredging portions of the lake was modeled to determine whether dredging of the lake provides additional flood protection benefits. Although the Elmendorf Lake Park improvements were conceptually designed to be compatible with flood- ing, the Pirnie/ARCADIS team was tasked with the responsibility to also look for viable options to reduce flooding within the constraints of the site and park planning process. Alternative 1 and a flood control gate at Elmendorf Lake Dam provide the greatest reduction in peak water surface elevations during flood events. Further study of the proposed flood control gate at the dam is recommended to evaluate the gate size and operation required to provide the most flood reduction. That study should also investigate the impact of flood flow releases on the area of Apache Creek downstream of the Elmendorf Lake Dam. 1.4 Water Quality Analysis Apache Creek and Elmendorf Lake are tributaries to the Upper San Antonio River Watershed (Texas Commission on Environmental Quality [TCEQ] Segment 1911). Segment 1911 is designated for contact recreation, although the City of San Antonio (COSA or “San Antonio”) has placed restrictions on swimming within the San Antonio River or its tributaries within the city limits. The segment also has a high aquatic use designation. Elmendorf Lake provides habitat for fish, turtle, and bird species. Water quality concerns within the study area include low dissolved oxygen, high bacterial loading (i.e., E. coli concentrations), elevated nutrient concentrations, high turbidity and floatable trash and debris follow- ing storm events, and periodic unpleasant odors. In previous studies, Lake dredging was identified as a 7 San Antonio River Authority Westside Creeks/Elmendorf Lake Final Report July 2012 SECTION 1 Executive Summary recommended approach to improve water quality and lake habitat, coupled with implementation of short and long-term storm water BMPs. Relevant data and studies were reviewed to confirm the primary water quality concerns to be addressed under the Conceptual Plan. The data and analyses are described in detail in Section 5. In summary, the data show several trends: • Dissolved Oxygen. Average dissolved oxygen concentrations for samples collected between 1983 and 2007 were above the Segment Specific State Standard (“State Standard”) at each sampling location. However, minimum dissolved oxygen concentrations measured at two sampling locations were below the State Standard. The measurements were also below concentrations required to support aquatic life. • Nutrients. Maximum measured concentrations for ammonia, nitrate and total phosphate in samples collected from one or more of the TCEQ locations were above the State nutrient screening criteria. El- evated nutrient concentrations can enhance algae growth in the lake and exacerbate eutrophic condi- tions, leading to a decrease in dissolved oxygen concentrations. • Total organic carbon. Total organic carbon (TOC) concentrations ranged from 2 to 25 milligrams per liter (mg/L). Organic matter (measured as TOC) can create an oxygen demand either through chemical or biological reactions. Accumulation of organic matter in the lake sediments can serve as a “sink” for continual consumption of dissolved oxygen within the lake. • Chlorophyll a. Chlorophyll a data are limited but generally show significant algal activity in the lake. Chlorophyll a is a pigment found in algae; concentrations of the pigment above 10 micrograms per liter (ug/L) can be used as a guideline for algal activity that can create quality issues for contact recreation. • E.Coli. Mean and peak E. coli concentrations measured at Elmendorf Lake are above the State Stan- dard for contact recreation, and the data show significant bacterial loading to the study area. Based on a review of available water quality data, sediment data and past studies, the primary water qual- ity concerns for Elmendorf Lake and Segment AP-1 are: • Dissolved oxygen concentrations below the State Standard during certain seasons and/or rainfall events with impacts to aquatic life; • E. coli concentrations several orders of magnitude above the State Standard for contact recreation; and • Sediment accumulation in the lake leading to reports of high turbidity during rain events and exacerbat- ing anoxic conditions. Additional concerns include nutrient concentrations above the State nutrient screening criteria and TOC concentrations exceeding 10 mg/L, both of which can exacerbate eutrophic conditions. Concentrations of certain synthetic organic compounds in the sediments are above the TCEQ health screening levels, but do not currently present an immediate health concern. Aesthetic concerns include accumulation of trash & debris following rain events and adverse odors, likely due to growth of blue-green algae and/or anoxic conditions in the lake. 8 San Antonio River Authority Westside Creeks/Elmendorf Lake Final Report July 2012 SECTION 1 Executive Summary SARA and Bexar County have identified lake dredging as one of the potential projects to restore and im- prove conditions in Elmendorf Lake. Recognizing the high cost and short-term benefit of dredging unless upstream stormwater best management practices (BMPs) are implemented, additional strategies to ad- dress water quality concerns were reviewed. Specifically, three technologies to increase dissolved oxygen concentrations in the lake were evaluated: • Aeration fountains, potentially installed in conjunction with air diffusers • SolarBee mixers • Side stream super-saturation • Water quality priorities must be carefully considered to select the most cost-effective approach to meet water quality goals for Elmendorf Lake and Apache Creek. Based on evaluation of historical water quality data, one of the most pressing concerns related to lake water quality is seasonal occurrence of low dis- solved oxygen concentrations in the lake, which can be detrimental to aquatic life and can reduce overall lake water quality. Dissolved oxygen in the lake could be increased in the short term at a relatively low cost by implementing one of various technologies on the market to add oxygen to the water. The installed system could continue to be used following implementation of stormwater BMPs and lake dredging. Sustainable stormwater BMPs discussed in Section 6 should be implemented for near-term reduction in trash & debris, nutrients, and TSS loading to the lake. Stormwater BMPS outlined in other SARA reports should also be considered to address additional water quality goals. Over the long term, BMPs should be incorporated to address a comprehensive set of water quality concerns, including: • Semi-volatile compounds and other synthetic organic compounds from storm water runoff; • Wise use of herbicides and pesticides in the watershed and especially right around the lake; • Bacteria and pathogenic microorganisms from pet wastes; • Nutrients and pathogens from any failure points within nearby sewer collection systems; and • Total suspended solids from construction activities and storm water runoff. Dredging to partially or fully restore the lake volume should be re-evaluated following implementation of initial stormwater BMPs, particularly if dissolved oxygen concentrations are increased in the near term through an oxygenation system. 1.5 Stormwater Best Management Practices One of the objectives of this evaluation was to recommend BMPs that can be employed to improve water quality and aesthetics in and around Elmendorf Lake. According to earlier studies performed for SARA, fo- cus should be placed on installing BMPs near the lake. Trash and other floatable debris were specifically mentioned as problems, and representatives of OLLU confirmed this. Section 6 of this report describes the methodology used to characterize the extent of effect on the Lake by various land use areas in the watershed, and it describes the types of BMPs recommended to manage stormwater runoff and improve its quality. The recommended BMPs range from public education and regulations to specific structural measures such as trash booms, catch basin inserts and netting devices. The report also discusses recommended sustainable BMPs related to low impact development techniques such as bioretention cells and rain gar- dens. 9 San Antonio River Authority Westside Creeks/Elmendorf Lake Final Report July 2012 SECTION 1 Executive Summary 1.6 Vision Plan Section 7 describes a conceptual vision developed by the Pirnie/ARCADIS team, SARA and its partners for the study area shown in Figure 7.4. By merging previous work with new creative thinking, we produced ideas and concepts for a cohesive sustainable solution that creates a Great People Place in the West- side. As this vision moves through the implementation process, more public input will be needed to final- ize the plan. As described in Sections 7 and 8 of this report, public investment by the COSA and Bexar County, and private investment by OLLU and others could be used to implement the vision. The proposed vision for the Elmendorf Lake reach of Apache Creek has connectivity as one of its primary focal points. The proposed plan reconnects valuable resources to their surroundings, to the community and the city. Perhaps the most crucial of all connections is between Elmendorf Lake Park, the lake and OLLU. The ulti- mate conceptual plan shown in Figure 1.1 (below considers Rosedale and Elmendorf Lake Parks as a unit linked by a hike and bike trail connection through the Apache Creek Linear Park. In a later phase Jose 10 Figure 1.1: Elmendorf Lake Conceptual Plan San Antonio River Authority Westside Creeks/Elmendorf Lake Final Report July 2012
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